The present disclosure relates generally to maintenance of condensate drain lines associated with air conditioners, refrigerators, ice makers and the like.
Drain lines for discharging condensate from air-conditioners, refrigerators, ice makers and other similar appliances tend to accumulate algae. In time, algae-build up can become a significant problem. For example, in air-conditioned apartment buildings with many individual air conditioning units, each of which units with its own condensate drain line, the algae deposits over time can clog the condensate drain lines. If a condensate drain line becomes clogged, the condensate will back up behind the algae plug. Eventually condensate may leak upstream of the plug and can cause water damage to the floor or to the ceiling of the apartment below. Although the algae clog can be removed by mechanical means—frequently, by using compressed air to blow the plug to the exterior so that the condensate flows freely again—the damage will have been done.
There is a need for a better way to manage condensate lines, that is, to keep them open so the condensate flows freely to the exit and, ideally, to enable the condensate lines to be self-cleaning.
According to its major aspects, the present device, when inserted in the condensate drain line, is useful in keeping condensate drain lines free of algae clogs, as long as the device itself is periodically replenished with an algaecide.
The device is connected in-line with an existing condensate drain line so the condensate stream flows through the device. The device is preferably installed nearer to the condensate source, well upstream from the end of the condensate drain line. The device thus becomes part of a flow path for the condensate, the condensate is treated for algae, and reenters the condensate drain line to continue its path to the environment—before algae concentrations in the drain line become large enough to plug the line.
The interior of the device is configured to facilitate interaction of the condensate with an algaecide. The residency time and flow path of the condensate in the device are designed to facilitate that interaction: that is, the inlet flow is directed by structures within the device toward the algaecide, and the outlet flow is retarded to increase interaction time with the algaecide, thereby facilitating the destruction of the algae and preventing algae from plugging the condensate tube and backing up in the condensate line and potentially damaging floors, ceilings, carpeting, and furniture.
An aspect of the device is a feed channel that contains a charge of algaecide, and holds that algaecide so that it descends to the bottom of the feed channel and into the condensate flow path where the algaecide reacts with the algae present to kill the algae. A charge of algaecide means a fixed quantity in any units of volume or mass, for example, added at one time, and that processes a quantity of algae effectively to preclude algae plugging for a conveniently large amount of time so that maintenance is convenient.
Another aspect of the disclosure is the reaction chamber of the device, which is located below the feed channel. The reaction chamber receives both the inflowing condensate and the descending algaecide in such a way that the algae present in the condensate is exposed to the algaecide and killed. The bottom of the feed channel, being just above the floor of reaction chamber, enables the algaecide at the bottom of the feed channel to mix with the condensate long enough to kill algae present. As the charge of algaecide in the feed channel is gradually used up, it descends further and further, urged by gravity, down the feed channel and into the reaction chamber. Meanwhile, the condensate continues to flow into the inlet of device so that there is always interaction between the algaecide and the condensate. A modest amount of experimentation will reveal the amount of algaecide to use in neutralizing the expected algae content in the condensate.
The feed channel and the corresponding quantity of algaecide are a feature of the application. These may be sized for typical rates of consumption and for specific appliances-such as for the window air conditioner or for mainframe computer rooms-and for the factors that contribute to more condensate flow or greater algae build-up, such as prevailing winds, temperatures, humidity, air quality, and so forth. These factors will inform the design of the present device for different circumstances so that a user will learn to add a new charge of algaecide on a more or less regular interval.
Another aspect of the feed tube is that the algaecide may be a solid or a thick gel that descends by gravity down the feed channel and into the reaction chamber where the lowest portion of the algaecide is exposed to the condensate for treatment. As the algaecide is consumed, the solid charge of algaecide continues to slowly descend down the feed channel until, eventually, it is used up or a new charge of algaecide is added to “top off” the remaining charge. A charge of solid algaecide is convenient to handle, package, and store. The solid may be in the form of a stick, granules, beads, or powder.
An aspect of the device is the reaction chamber where the flow of incoming condensate is guided by flow diverters so condensate flows from the inlet of reaction chamber to the outlet and, along its path, is exposed to the algaecide to permit interaction with the algaecide, namely, killing typcial algae to reduce the likelihood that an algae plug will form in the condensate tube.
An aspect of the device is that it includes structures—namely, flow diverters—engineered to cooperate with the inlet and the outlet and feed channel in accomplishing the particular purpose for which the device is intended, namely, one-way flow through the device that effectively exposes condensate to the algaecide.
Also, the device itself is easy to install in the condensate line, preferably, at the beginning of the condensate line, where the device is likely more accessible and the algaecide can easily and conveniently be recharged.
These and other features and their advantages will be apparent to those skilled in the art of condensate drain line maintenance from a careful reading of the present disclosure.
Referring now to the figures,
Device 20 permits controlled interaction between condensate and an algaecide so as to kill the algae that may be present in the condensate and thereby preclude plugging of condensate drain line 32 by preventing the formation of a mass of algae.
Referring now to
Device 20 includes reaction chamber 24 with an inlet 44 on a first side 46 of reaction chamber 24 that receives condensate from upstream condensate line 28, and includes an outlet 48 on a second side 50 of reaction chamber 24 that delivers condensate received from inside reaction chamber 24 to condensate drain line 32 on the other side of reaction chamber 24. To assure flow of condensate between inlet 44 and outlet 48, inlet 44 enters reaction chamber 24, which is elevated above floor 54 slightly with respect to outlet 48 which is set closer to floor 54 of reaction chamber 24, as best seen in
A feed channel 56 communicates with the interior of reaction chamber 24 and extends above it. Feed channel 56, which may include a lid 60, is dimensioned to receive a charge of algaecide 58 that is a solid or semisolid, as seen in
Reaction chamber 24 may include diverters 68 for controlling the direction and for slowing the movement of condensate through reaction chamber 24 from inlet 44 across reaction chamber 24 though outlet 48, to facilitate the engagement of the moving condensate with the bottom of algaecide 58.
At inlet 44 of the reaction chamber 24, condensate is guided by inlet diverters 68 that channel condensate flow toward algaecide 58 which has descended feed channel 56 and rests on the floor 54 of reaction chamber 24. Algaecide 58 is positioned in reaction chamber 24 to receive the flow of the condensate from inlet diverters 68. As the condensate interacts with algaecide 58, a portion of algaecide 58 mixes with the condensate and reacts with algae in the condensate. As it does, additional algaecide 58 moves to rest on floor 54 and engage the continued flow of condensate. The algae in the condensate reacts with algaecide 58 as it continues to move toward outlet 48. An outlet diverter 72 slows the condensate in order to facilitate the completion of the interaction between algaecide 58 and condensate. The condensate then passes through outlet 48 of reaction chamber 24.
Additional algaecide 58 may be added from time to time to feed channel 56. It may be added, for example, by placing a quantity in the form of a solid “stick” or block periodically into feed channel where the algaecide stick descends by gravity into position engaging floor 54 of reaction chamber 24 where the lowest portion of algaecide 58 makes contact with the flow of condensate and is consumed by the reaction with the algae. As algaecide 58 is consumed, algaecide 58 continues its decent. Algaecide 58 can continue to react with the algae in the condensate for a period of time, which may be days or weeks, or a month. Periodically then, algaecide 58 feed channel 56 will need to be replenished simply by inserting a charge of algaecide 58 into feed channel 56.
Algaecide may be in the form of a solid prism, as shown, in
The long dimension of the algaecide in the form of a stick or rod may then conveniently serve as a measure of rate of use (as the equivalent of sand in an hourglass), to measure the time left before the stick is consumed and will need to be replaced. The cross-sectional area will be the interaction area with the condensate forwarded by the flow from the inlet diverters. Outlet diverter 72 in part cooperates with inlet diverters 68 to urge condensate to react with algaecide. A modest amount of calculation and experimentation will enable those of ordinary skill to coordinate the size, number and spacing of inlet diverters 68 and outlet diverter 72, the relative heights of inlet 44 with respect to outlet 48 and cross section and height of feed channel 56 required to reduce the algae population of a typical condensate flow in different environments to prevent algae agglomeration and plugging of condensate lines.
A cap 60 on feed channel 56 allows algaecide 58 to remain clean. On removal of cap 60, a user can, by observing the extent algaecide 58 has been depleted by how far from the cap 62 of feed channel 56 algaecide 58 descended since feed channel 56 was last filled, determine the approximate rate of use. Optionally, feed channel 56 may be marked with gradations to permit a more precise estimation of days remaining until replacement algaecide 58 will be needed.
Algaecide 58 may be in a solid or a liquid form. A mild acid such as a chlorine (ClO2), such as “pool” chlorine can be obtained in solid form such as a stick, a rod, or a powder; or alternatively, algaecide 58 may be a liquid acid such as vinegar (CH3COOH), or it may be a proprietary, biodegradable, algae-controlling compound, or a combination of algaecides. A combination of liquid chlorine and vinegar, for example, may be used provided care is taken. Also, algaecide 58, if in solid form, may be shaped so as to increase exposure to the condensate, such as by having a spiral exterior groove or vertical channels.
In use, device 20 is first attached to a condensate drain line 32. Device 20 may be attached to the end of condensate line nearest to the source of the condensate as shown in
Inserting device 20 in a condensate drain line 32 running from the appliance that generates the condensate requires drain line 32 to be cut in order to insert device 20. The upstream end at that cut is then attached to inlet 44 of device 20. The downstream end at the same cut is then attached to the outlet 48 of device 20.
Once in use, feed channel 56 of device 20 may be checked periodically, more often during in wet humid weather and less often in cooler dryer weather, to determine the rate at which algaecide is being depleted. The connections and general functioning the device 20 should also be checked. In apartment complexes, feed channels 56 for device 20 may be simply topped up periodically with algaecide 58. Device 20 may be inspected for connections, during which inspection, cap 60 is removed and feed channel 56 is inspected for depletion of algaecide 58.
In one embodiment, the system described herein relate to a device, including: a reaction chamber having a floor, an inlet wall, an outlet wall, a first side wall and a second side wall, wherein the floor, the inlet wall, the outlet wall and a side wall defining the first side wall and the second side wall define an interior of the reaction chamber; a chamber inlet defined in the inlet wall adapted to provide a flow of a condensate into the interior; a chamber outlet defined in the outlet wall, the chamber inlet and the chamber outlet, the chamber inlet and the chamber outlet being dimensioned to connect to a condensate inlet line and a condensate outlet line for receiving a flow of the condensate into the interior and out of the chamber outlet; an algaecide disposed in the interior and positioned to interact with the condensate entering the interior; and, an outlet flow diverter disposed between the algaecide and the chamber outlet, wherein the outlet flow diverter has a width that is less than a diameter of the chamber outlet and the outlet flow diverter is positioned within the reaction chamber so that the width does not extend past the chamber outlet and does not touch the first side wall and the second side wall so that condensate that flows past the outlet flow diverter may flow into the chamber outlet without obstruction by the outlet wall.
In one embodiment, the system described herein relate to a device including a inlet flow diverter disposed under the chamber inlet and adapted to focus the condensate toward the algaecide.
In one embodiment, the system described herein relate to a device including a feed channel extending into the reaction chamber.
In one embodiment, the system described herein relate to a device wherein the feed channel includes an opening and the algaecide is dimensioned to fit inside the feed channel.
In one embodiment, the system described herein relate to a device wherein the algaecide incudes a first side having a larger surface than an opposite side included in the algaecide.
In one embodiment, the system described herein relate to a device wherein the algaecide is selected from the group consisting of chlorine, calcium hypochlorite, acid, and any combination thereof.
In one embodiment, the system described herein relate to a device wherein the algaecide is a liquid and a feed channel in fluid communication with the reaction chamber.
In one embodiment, the system described herein relate to a device wherein the feed channel includes a bottom with a weep hole for the liquid to drip through.
In one embodiment, the system described herein relate to a device wherein the algaecide is a prism shape algaecide.
In one embodiment, the system described herein relate to a device wherein the reaction chamber includes a feed channel in fluid communication with the reaction chamber and dimensioned to accept the prism shape algaecide.
In one embodiment, the system described herein relate to a device wherein the feed channel includes a bottom with an opening leading to the floor of the reaction chamber and dimensioned to allow the prism shape algaecide to contact and rest in the floor of the reaction chamber.
In one embodiment, the system described herein relate to a device where the prism shape algaecide includes a triangular cross section, and the feed channel is dimensioned to position a lateral face of the prism shape algaecide towards the chamber inlet and an edge of the prism shape algaecide towards the chamber outlet.
In one embodiment, the system described herein relate to a device wherein the outlet flow diverter is dimensioned and spaced in relation to the chamber outlet to slow a movement of condensate away from the chamber outlet.
In one embodiment, the system described herein relate to a device wherein the outlet flow diverter directs flow of the condensate from the reaction chamber away from the chamber outlet.
In one embodiment, the system described herein relate to a device wherein the inlet flow diverter is oriented to direct the condensate toward the algaecide wherein the inlet flow diverter is adapted to increase an interaction between the condensate and the algaecide.
In one embodiment, the system described herein relate to a device wherein the inlet flow diverter is adapted to redirect the flow of the condensate toward a lateral face of the algaecide.
In one embodiment, the system described herein relate to a device, including: a reaction chamber having a floor, a side wall and an outlet wall; a chamber inlet defined in the reaction chamber positioned at a first distance above the floor; a chamber outlet defined in the reaction chamber positioned at a second distance above the floor wherein the first distance is higher than the second distance; an algaecide positioned in the reaction chamber and adapted to interact with a condensate entering the reaction chamber; and, an outlet flow diverter attached to the reaction chamber and does not touch both the first side wall and the second side wall and has a width that is less than the width of the outlet wall, the outlet flow diverter being positioned adjacent to the chamber outlet and adapted to direct at least a portion of the second flow of the condensate away from the chamber outlet.
In one embodiment, the system described herein relate to a device including an inlet flow diverter attached to the reaction chamber and disposed under the chamber inlet wherein the inlet flow diverter is positioned adjacent to the chamber inlet, and focus the condensate toward the algaecide.
In one embodiment, the system described herein relate to a device including a set of inlet flow diverters adapted to slow a movement of condensate in the reaction chamber.
In one embodiment, the system described herein relate to a device, including: a reaction chamber having a floor and a side wall; a chamber inlet defined in the reaction chamber operatively associated with an inlet flow diverter, the inlet flow diverter being attached to the reaction chamber and the inlet flow diverter focuses a flow of condensate toward an algaecide disposed in the reaction chamber; and, a chamber outlet defined in the reaction chamber operatively associated with an outlet flow diverter that does not touch the side wall so that the outlet flow diverter obstructs at least a central portion of the chamber outlet and directs at least a portion of the flow of condensate away from the central portion of the chamber outlet.
In one embodiment, the system described herein relate to a device wherein the outlet flow diverter is positioned at an outlet angle relative to a long axis of the outlet flow diverter and an outlet wall defined in the reaction chamber.
In one embodiment, the system described herein relate to a device wherein the inlet flow diverter is positioned to direct movement of the condensate toward a lateral face of the algaecide.
In one embodiment, the system described herein relate to a device wherein the inlet flow diverter extends upward from the floor.
In one embodiment, the system described herein relate to a device wherein the outlet flow diverter extends upward from the floor.
Those skilled in the maintenance of drain lines will appreciate, from a careful reading of the foregoing detailed description, many advantages of the feature described and the many savings in time and effort to manage multiple drain line, particularly in warmer, moister climates where air conditioning is widely used.
This application is a continuation of United Staes patent application Ser. No. 17/383,008 filed 7/22/2021.
Number | Date | Country | |
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63075629 | Sep 2020 | US |
Number | Date | Country | |
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Parent | 17383008 | Jul 2021 | US |
Child | 18950041 | US |